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<br />MANAGEMENT BRIEF <br /> <br />203 <br /> <br />ASMR 3 <br /> <br />ASMR 3 differs from formulations 1 and 2 in that <br />more flexibility is allowed in the estimation of age- and <br />time:specific capture probabilities (fi a)' As in ASMR <br />2, U T is estimated directly; however, we use the <br />conditional maximum likelihood estimate for the P <br />a,l <br />matrix, that is, <br /> <br />^ rna,l + ra.t <br />Pa.t = ^. ^ . <br />. Ua,t + Ma,t <br /> <br />This formulation eliminates the need to specify annual <br />vulnerability schedules at the expense of a much larger <br />parameter set. ASMR 3 maximizes equation (6) by <br />varying e = (M'adull and Ua.T). <br />One strength of the overall ASMR approach is that it <br />allows the estimation of recruit abundance for years <br />preceding the onset of data collection by using age- <br />specific survival rates and initial-year abundance as <br />follows: <br /> <br />^ Ua.l <br />U2,2-a = ~. <br />nSj <br />t=2 <br /> <br />This is an important aspect of the ASMR and <br />a distinction from the "recruitment" parameter esti- <br />mated by Jolly-Seber type methods (discussed below). <br /> <br />Assignment of Apparent Age at First Capture <br /> <br />We reparameterized the polynomial length-at-age <br />relationship contained in the humpback chub Endan- <br />gered Species Act recovery goals and based on fish <br />collected in Grand Canyon (USFWS 2002) to a von <br />Bertalanffy growth function necessary for the Lorenzen <br />mortality curve. We then used the inverse von <br />Bertalanffy growth function to assign apparent age as <br />a function of length, that is, <br /> <br />a=-~log,,(I-f)-ao, (11) <br /> <br />where k=0.12, ao =0.87, and I", =455. We conducted <br />sensitivity analyses on the effect of growth parameter <br />misspecification on abundance and recruitment trends. <br /> <br />Model Performance <br /> <br />We tested the estimation methods by generating <br />simulated capture-recapture data from known numbers <br />of fish Ua,l and U2,t from ages 2-30 and years 1989- <br />2002 subject to individual binomial capture, survival, <br />and recapture events over age and time with known va.1 <br />and annual capture probabilities (fi/)' These tests <br />indicate that the method gives unbiased estimates of <br />the PI' Ua,l up to at least age 10, the U2,1 for all t, Va,1 for <br />the time periods mentioned above, and age-specific <br />survival rates Sa up to at least a = 20. The simulated <br /> <br />(9) <br /> <br />recruitment and initial stock estimates U2,t and Ua.l are <br />precise (<10% error) for the period from the early to <br />the mid 1990s and become imprecise for the late 1990s <br />to 2002. Most S estimates are precise for all a. <br />a <br />We cannot assign an accurate age to each humpback <br />chub at first capture. The recapture size data indicate <br />that growth rates are extremely variable; for example, <br />the average size of an age-l0 humpback chub is around <br />300 mm TL, but fish of this size can be anywhere <br />between about 6 and 15 years of age. When we assign <br />a fish an "age" at first capture, that age may well be <br />predictive of the subsequent size-dependent survival <br />rate (Lorenzen model) but is probably not the correct <br />age for assigning the fish to a cohort. This means that <br />the y,7ar-class strengths or apparent cohort sizes Ua,l <br />and U2,1 estimated by the procedure outlined above are <br />not the numbers of fish recruiting or initially present by <br />cohort but rather some smoothed or running average of <br />the actual cohort strengths. The estimation method <br />should still be able to detect longer-term trends in <br />abundance and recruitment, but it is less able to detect <br />subtle changes in year-class strength. <br />The use of VP A back propagation for calculating Ua,1 <br />does not cause the ASMR method to overestimate adult <br />abundance. To evaluate this, we replaced equation (3) <br />with the forward prediction equation (1) for U and <br />A 0.1 <br />included th,7 initial unmarked abundances Ua,l (a = 2, . . <br />.,30) and U2,I (t > 1) in the set ofunIrnown parameters <br />to be estimated by maximizing equation (6). This <br />resulted in essentially the same abundance and adult <br />mortality estimates as the back propagation method. <br />While the proposed estimation method is unbiased <br />when supplied with accurate ages at first capture, tests <br />with simulated data lhat include initial aging error <br />indicate lhat it produces estimates of A. and M'adUlt that <br />are biased downward by about 7% and 11 %, re- <br />spectively. However, it still tracks the simulated <br />recruitment patterns over time and does not create <br />a spurious simulated trend in back-calculated recruit- <br />ments before lhe first year of sampling (Figure I). <br />As a measure of uncertainty, we sampled lhe <br />posterior distribution of the parameter estimates using <br />Markov chain-Monte Carlo (MCMC) techniques for <br />each ASMR formulation. Following Gelman et al. <br />(2000), we constructed 95%-credible intervals from <br />MCMC parameter chains of length 1,000 from 200,000 <br />MCMC trials, retaining every l00th trial and disre- <br />garding the first half of lhe chain. We assessed <br />convergence using Gelman and Rubin's potential scale <br />reduction factor (R Development Core Team 2005). <br /> <br />Discussion <br /> <br />The abundance and mortality trends from lhe ASMR <br />and Jolly-Seber models are similar (Coggins et al. <br /> <br />(10) <br />